US20020043482A1 - Process for desulfurization of petroleum distillates - Google Patents
Process for desulfurization of petroleum distillates Download PDFInfo
- Publication number
- US20020043482A1 US20020043482A1 US09/735,839 US73583900A US2002043482A1 US 20020043482 A1 US20020043482 A1 US 20020043482A1 US 73583900 A US73583900 A US 73583900A US 2002043482 A1 US2002043482 A1 US 2002043482A1
- Authority
- US
- United States
- Prior art keywords
- sulfur
- compounds
- fraction
- ppm
- diesel
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims abstract description 37
- 230000008569 process Effects 0.000 title claims abstract description 36
- 238000006477 desulfuration reaction Methods 0.000 title abstract description 15
- 230000023556 desulfurization Effects 0.000 title abstract description 15
- 239000003209 petroleum derivative Substances 0.000 title abstract description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 94
- 150000003464 sulfur compounds Chemical class 0.000 claims abstract description 13
- 125000004122 cyclic group Chemical group 0.000 claims abstract description 4
- 239000011148 porous material Substances 0.000 claims abstract description 4
- 229910052717 sulfur Inorganic materials 0.000 claims description 166
- 239000011593 sulfur Substances 0.000 claims description 164
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 130
- 229910052799 carbon Inorganic materials 0.000 claims description 67
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 claims description 48
- 239000002904 solvent Substances 0.000 claims description 32
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 claims description 27
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 17
- 239000002283 diesel fuel Substances 0.000 claims description 17
- 229910052757 nitrogen Inorganic materials 0.000 claims description 8
- 239000007789 gas Substances 0.000 claims description 6
- RGSFGYAAUTVSQA-UHFFFAOYSA-N Cyclopentane Chemical compound C1CCCC1 RGSFGYAAUTVSQA-UHFFFAOYSA-N 0.000 claims description 4
- -1 naphtha Substances 0.000 claims description 4
- 125000003118 aryl group Chemical group 0.000 claims description 2
- 150000008280 chlorinated hydrocarbons Chemical class 0.000 claims description 2
- 239000010779 crude oil Substances 0.000 claims description 2
- 239000000295 fuel oil Substances 0.000 claims description 2
- 239000003502 gasoline Substances 0.000 claims description 2
- DMEGYFMYUHOHGS-UHFFFAOYSA-N heptamethylene Natural products C1CCCCCC1 DMEGYFMYUHOHGS-UHFFFAOYSA-N 0.000 claims description 2
- 239000003350 kerosene Substances 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims 9
- 239000003208 petroleum Substances 0.000 claims 9
- 239000007800 oxidant agent Substances 0.000 claims 3
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims 2
- 238000004064 recycling Methods 0.000 claims 2
- 239000003570 air Substances 0.000 claims 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims 1
- 229910052760 oxygen Inorganic materials 0.000 claims 1
- 239000001301 oxygen Substances 0.000 claims 1
- 238000011069 regeneration method Methods 0.000 abstract description 7
- 238000001179 sorption measurement Methods 0.000 abstract description 7
- 230000008929 regeneration Effects 0.000 abstract description 6
- 239000003960 organic solvent Substances 0.000 abstract description 2
- 239000003921 oil Substances 0.000 description 35
- 230000002829 reductive effect Effects 0.000 description 21
- 239000002002 slurry Substances 0.000 description 16
- 239000000047 product Substances 0.000 description 9
- 238000004821 distillation Methods 0.000 description 6
- 238000009826 distribution Methods 0.000 description 6
- 239000000446 fuel Substances 0.000 description 6
- 238000005259 measurement Methods 0.000 description 6
- GCLGEJMYGQKIIW-UHFFFAOYSA-H sodium hexametaphosphate Chemical compound [Na]OP1(=O)OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O1 GCLGEJMYGQKIIW-UHFFFAOYSA-H 0.000 description 6
- 238000011084 recovery Methods 0.000 description 5
- 238000009833 condensation Methods 0.000 description 4
- 230000005494 condensation Effects 0.000 description 4
- 230000004048 modification Effects 0.000 description 4
- 238000012986 modification Methods 0.000 description 4
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- 238000009835 boiling Methods 0.000 description 3
- 239000003054 catalyst Substances 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 238000010926 purge Methods 0.000 description 3
- FCEHBMOGCRZNNI-UHFFFAOYSA-N 1-benzothiophene Chemical compound C1=CC=C2SC=CC2=C1 FCEHBMOGCRZNNI-UHFFFAOYSA-N 0.000 description 2
- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- IYYZUPMFVPLQIF-UHFFFAOYSA-N dibenzothiophene Chemical compound C1=CC=C2C3=CC=CC=C3SC2=C1 IYYZUPMFVPLQIF-UHFFFAOYSA-N 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 230000000670 limiting effect Effects 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 230000001105 regulatory effect Effects 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 238000010998 test method Methods 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- ZHBBDTRJIVXKEX-UHFFFAOYSA-N 1-chloro-2-(3-chlorophenyl)benzene Chemical compound ClC1=CC=CC(C=2C(=CC=CC=2)Cl)=C1 ZHBBDTRJIVXKEX-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 241000428199 Mustelinae Species 0.000 description 1
- 238000000944 Soxhlet extraction Methods 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000003849 aromatic solvent Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 230000036961 partial effect Effects 0.000 description 1
- 238000005504 petroleum refining Methods 0.000 description 1
- 239000002798 polar solvent Substances 0.000 description 1
- 238000005498 polishing Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000011877 solvent mixture Substances 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 238000005292 vacuum distillation Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G25/00—Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G25/00—Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
- C10G25/003—Specific sorbent material, not covered by C10G25/02 or C10G25/03
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G25/00—Refining of hydrocarbon oils in the absence of hydrogen, with solid sorbents
- C10G25/12—Recovery of used adsorbent
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G53/00—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes
- C10G53/02—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes plural serial stages only
- C10G53/08—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes plural serial stages only including at least one sorption step
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G53/00—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes
- C10G53/02—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes plural serial stages only
- C10G53/14—Treatment of hydrocarbon oils, in the absence of hydrogen, by two or more refining processes plural serial stages only including at least one oxidation step
Definitions
- the present invention relates to a novel process for the removal of sulfur compounds from petroleum distillates by selective adsorption on activated carbon which can be used in petroleum refining for the desulfurization of gasoline, naphtha, kerosene, diesel fuel, fuel oil and other products.
- U.S. Pat. No. 5,454,933 teaches a process that uses activated carbon together with catalysts composed of Group VI and Group VIII metals as a polishing desulfurization agent for distillates previously subjected to hydrodesulfurization.
- U.S. Pat. No. 2,877,176 teaches the use of alkali-doped activated carbon for adsorption of sulfur from distillate fuels followed by washing the carbon with a hot hydrocarbon.
- negligible amounts of activated carbon impregnating a catalyst within the carbon to create its activation
- other reagents which results in reduced emissions into the environment is not disclosed or described in the prior art.
- the present invention relates to a process for desulfurization of petroleum distillates, in particular diesel fuel separated by distillation into a low sulfur and a high sulfur fraction, using cyclic low temperature adsorption of the high sulfur diesel fraction on commercially available activated carbon (catalytically impregnated carbon) followed by a solvent stripping step, a regeneration (solvent-washing) step and a carbon drying step in a closed loop zero emission system.
- the desulfurized diesel fuel is then blended with the low-sulfur diesel fraction from the primary crude separation (distillation) step to yield the final desulfurized diesel product and a high-sulfur by product.
- FIG. 1 is a diagrammatic flowchart of the overall process' concept as provided in accordance with the teachings of the present invention. Specifically FIG. 1 shows the initial process whereby diesel fuel is split into low-sulfur and high-sulfur fractions.
- FIG. 2 is a detailed flowchart of the overall desulfurization process of the high-sulfur fraction as provided in accordance with the teaching of the present invention.
- FIG. 1 crude oil 1 is first subjected to distillation 2 to achieve the various fractions 3, 4, 5 of which diesel 3 is one. Diesel typically ranges from approximately C 10 to C 20 hydrocarbons. Approximately 30% of the diesel fraction from C 10 to C 13 contains much less sulfur than the heavier fraction (C 14 to C 20 ). The high-sulfur 4 fraction is then subjected to the process shown in FIG. 2.
- the high-sulfur diesel fraction or diesel feed 21 mixes with the high-sulfur bottom recycle 41 as shown in FIG. 2.
- the combined stream 22 enters the sulfur adsorber 43 either co-currently or counter-currently.
- the sulfur adsorber 43 consists of a moving-bed of high surface area (between approximately 500 to 1500 m 2 /g) porous (with most pores in the 10 to 100 Angstrom range) carbon.
- the diesel fuel is desulfurized and leaves the adsorber 43 as low-sulfur diesel product 23 to be blended with the low sulfur diesel fraction 3 from FIG. 1.
- the moving carbon stream 25 enters a solvent stripper 44 into which a solvent vapor laden nitrogen stream 27 enters and essentially solvent-free nitrogen stream 28 leaves.
- the carbon 26 moves out of the solvent stripper 44 as stream 26 and enters the oil desorber 45 where it is contacted with liquid solvent and leaving with the desorbed oil as stream 30 .
- the solvent and oil mixture 30 goes to a solvent still 46 and is separated into a high-sulfur bottom stream 42 and a solvent overhead stream 35 that is recycled back to the oil desorber as stream 29 .
- the high-sulfur bottom recycle stream 41 can be recycled to the mix with the diesel as stream 22 to increase the sulfur content of the feed to the sulfur adsorber 43 and reduce the amount of oil carried away in the high-sulfur bottom stream 42 .
- the regenerated carbon leaves the oil desorber as stream 31 and since it contains solvent it enters a solvent desorber 47 .
- the solvent is stripped from the carbon by nitrogen stream 28 and the nitrogen solvent mixture 27 is recirculated back to the solvent stripper 44 .
- the dry regenerated carbon leaves the solvent desorber as stream 24 and is recycled back to the sulfur adsorber 43 .
- the entire process takes place at pressures ranging from approximately 1-5 atmospheres.
- Solvent stripper 46 25-50° C.
- Solvents used in conjunction with the teachings of the present invention include organic solvents with boiling points below the boiling point of the petroleum distillate to be desulfurized.
- the petroleum distillate is diesel fuel having an initial boiling point of approximately 150° C.
- Toluene is the preferred solvent for desulfurizing diesel fuel.
- Other acceptable solvents include, but are not limited to, benzene, chlorinated hydrocarbons, hexane and cyclopentane.
- environmental and toxicity concerns may limit the choice of industrially acceptable solvents. Solvents are selected based upon their ability to remove aromatic components of oxidized sulfur.
- the diesel fuels used were gas oil 0.2% S from Saybolt (Diesel #1), L-0, 2-62 premium from Lukoil (Diesel #2), and L-0, 5-62 from Lukoil (Diesel #3).
- the properties of these fuels as provided by the supplier are shown in Table 1.
- Diesel #1 was analyzed 10 times using the Horiba analyzer. The average sulfur content was 1353 ppm with a standard deviation of 18 ppm.
- the Diesel #2 was analyzed 10 times using the Horiba analyzer.
- the average sulfur content was 1969 ppm with a standard deviation of 12 ppm.
- Diesel #3 was analyzed 10 times using the Horiba analyzer. The average sulfur content was 2847 ppm with a standard deviation of 26 ppm.
- Example 1 was repeated using 467.12 g of Diesel #3 that measured at 2850 ppm sulfur. The weight distribution and sulfur contents are provided below.
- Example 1 was repeated using 261.44 g of Diesel #1 that measured 1353 ppm sulfur.
- the weight distributions and sulfur contents are provided below: Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.45 NM collected from vapor by condensation at ⁇ 2 C. 2 19.88 582 164 3 24.17 828 193 4 20.88 1150 212 5 2.43 1418 223 6 29.19 2574 Residual Diesel
- Example 1 was repeated using 470.11 g of Diesel #1 that measured 1357 ppm sulfur. Seven fractions were collected. The weight distributions and sulfur contents are provided below. Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.83 379 collected from vapor by condensation at ⁇ 2 C. 2 10.2 518 143 3 10.63 723 152 4 11.97 795 167 5 9.79 846 181 6 4.15 860 194 7 51.65 1987 Residual Diesel
- Example 1 was repeated using 818.69 g of Diesel #3 that measured 2850 ppm sulfur.
- the weight distributions and sulfur contents are provided below: Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.85 NM 2 10.94 489 184 3 8.29 622 197 4 9.64 982 203 5 3.77 1123 207 6 66.50 3884 Residual Diesel
- a quantity of 41.72 g of residual diesel (3884 ppm sulfur) from Example 6 was placed in each of 5 different beakers. Ten grams of carbons A, B, C, D and E were mixed into the 5 beakers respectively. The sulfur levels in the free oil was measured and the measurements are shown below: Sulfur remaining (ppm) Carbon After 4.3 h After 24.1 h A — 3904 B — 3071 C — 3065 D — 3134 E 3572 3357
- a large sample of Diesel #1 was distilled as in Example 1 to produce 5 fractions and 1584 g of residual diesel. Fractions 1 and 2 were combined to yield 440 g; fractions 3, 4, and 5 were combined to yield 1018 g.
- the residual diesel measured 1992 ppm sulfur.
- the 1584 g of residual diesel was placed in a 4 L beaker and approximately 396 g of Carbon B was added. After 72 hours, the sulfur content was reduced to 1330 ppm.
- the resulting diesel was filtered to yield 1313 g of oil with 271 g of oil retained on the carbon. To the 1313 g of diesel, approximately 326 g of fresh Carbon B was added and the slurry which was left standing for 72 hours. The sulfur content was reduced to 980 ppm.
- the resulting slurry was filtered and 1096 g of oil was recovered. To this oil, 271 g of Carbon F was added and left standing for an additional 24 hours. The sulfur content was reduced to 797 ppm. This slurry was filtered and 880 g of oil was recovered. To this, 222 g of Carbon C was added and left standing for another 24 hours. The sulfur content was reduced to 635 ppm. The resulting slurry was filtered and yielded 689 g of oil. To this, 70 g of Carbon C and 102 g of Carbon D was added. The sulfur reduced to 531 ppm. This final slurry was filtered to yield 554 g of oil.
- the combined fractions 3-5 from Example 10 (1018 g) measured 773 ppm sulfur.
- the combination was placed in a beaker and 252 g of Carbon F was added. After 24 hours the sulfur content had reduced to 612 ppm.
- the slurry was filtered and 829 g of oil was recovered. To this slurry 206 g of Carbon F was added. After 24 hours the sulfur content had been reduced to 515 ppm.
- the slurry was filtered and 688 g of oil was recovered. To this 171 g of Carbon D was added. After 24 hours the sulfur content had been reduced to 488 ppm.
- the slurry was filtered and 570 g of oil was recovered.
- 38.7 g of Carbon D was added.
- To this 33 g Carbon D was added.
- the sulfur content was reduced to 845 ppm.
- the slurry was filtered to yield 113 g oil.
- a quantity of 72 g of spent carbon (with oil) [from Example 10, Carbon C added to 797 ppm sulfur oil] containing an estimated 33 g oil was subjected to Soxhlet extraction using toluene
- the toluene (with oil extracted) was distilled to separate the oil that measured 31.5 g and had 1261 ppm sulfur.
- the carbon was dried with nitrogen gas at 120° C.
- the regenerated carbon was tested for desulfurization efficiency. Forty-one g of regenerated carbon was mixed with 171 g of Diesel #3 containing 2835 ppm sulfur. The sulfur content was reduced to 1949 ppm in 24 hours. The regenerated carbon was thus more efficient than the original carbon.
- a quantity of 50 g of Diesel #3 (2850 ppm sulfur) was mixed with approximately 20 g of Carbon G. After 15 minutes of contact with stirring, the slurry was filtered with a recovery of 33 g of diesel. Its sulfur value had dropped to approximately 2201 ppm and 17 g of Diesel #3 remained attached to the wet carbon externally (in between granules) and inside the pores. The original Diesel #3 color was yellow and the diesel recovered was yellow.
- Fifty (50) g of hexane was poured through the wet carbon and 41 g of hexane wash came through the carbon with 9 g remaining on the carbon. The hexane wash was clear, not yellow, and contained approximately 422 ppm sulfur.
- Example 25 was repeated except Carbon F was substituted for Carbon G.
- the diesel recovered from the carbon weighed 36 g. It had 2374 ppm sulfur and its color was yellow.
- the hexane wash weighed 41 g, it was colorless and had 266 ppm sulfur.
- the toluene wash weighed 45 g, it was light yellow and it had 218 ppm sulfur.
- An upflow packed-column was prepared containing about 2200-cc (1238 g) of carbon G.
- the column was a 2.5-inch ⁇ 36-inch high stainless steel tube. External controlled heat was supplied to the column if necessary to control the bed temperature.
- the diesel flow to the column was set at 17.2 cc/min. A number of diesel fuel samples were tested.
- the sulfur was reduced from 483 ppm to 60-129 ppm for the first 800 ml of fuel that passed through the column, over about 45 minutes.
- Example 27 The sulfided column from Example 27 was regenerated with toluene upflow (13 cc/min) for two hours at 75° C. The sulfur content in the toluene product and column toluene drain indicated a sulfur recovery from the column of 73%. Following the toluene wash, column was purged with nitrogen for two hours at 100° C.
- Example 30 The partially regenerated column of Example 30 was tested for recovery of desulfurization efficiency.
- a diesel sample Diesel #2, Table 1 containing 1998 ppm sulfur was flowed up through the column at conditions similar to Example 27. Seven 200 cc batches and the column drain were collected and their sulfur content was measured as follows: Sulfur (ppm) Batch 1 462 Batch 2 558 Batch 3 726 Batch 4 881 Batch 5 962 Batch 6 1084 Batch 7 1152 Column Drain 1676
- Example 31 The column from Example 31 was regenerated again as in Example 30 with toluene followed by a nitrogen purge. Measurement of sulfur in the toluene effluent and column drain indicated an 86% recovery of the sulfur from the column.
- Example 32 The partially regenerated column of Example 32 was tested using a 526 ppm sulfur-containing diesel feed at conditions similar to Example 27.
- the first 250-ml effluent contained 413-ppm sulfur and the column drain contained 506-ppm sulfur.
- Examples 31 and 33 indicate that following regenerations, sulfur removal limit is around 500 ppm. This suggested a modification to the regeneration procedure.
- Example 33 The column from Example 33 was regenerated as in Example 30 with toluene, however, the nitrogen purge was conducted at a higher temperature of 115° C.
- Example 34 The partially regenerated column of Example 34 was again tested using the 526-ppm sulfur containing diesel feed at conditions similar to Example 27.
- the first 280 ml and the next 125 ml sample effluents showed only 300 ppm sulfur as opposed to 413 ppm in Example 33 and the column drain showed 440 ppm as opposed to 506 ppm sulfur in Example 33. This suggests that the 15° C. higher N 2 purge temperature improved the regeneration efficiency of the column.
- Example 35 The column of Example 35 was regenerated as in Example 34.
- the partially regenerated column was tested using a 534-ppm sulfur containing diesel feed, in a manner similar to Example 27, except that the column was maintained at 70° C. as opposed to 30° C. in Example 27.
- a total of 12 samples of the product and the column drain were collected from the effluent as shown below.
- Example 36 The column from Example 36 was again regenerated as in Example 35 and subjected to diesel feed containing 485 ppm sulfur in a manner similar to Example 27, except that the temperature was 63° C. and flow was reduced from 17.2 ml/min to 6.3 ml/min. A total of 12 samples of the product and the column drain were collected from the effluent as shown below. Amount (g) Sulfur (ppm) Sample 1 129 249 Sample 2 117 277 Sample 3 116 261 Sample 4 121 260 Sample 5 123 263 Sample 6 123 278 Sample 7 120 288 Sample 8 131 322 Sample 9 123 293 Sample 10 120 317 Sample 11 121 284 Sample 12 128 354 Column Drain 711 468
- the present invention provides a simple, mild, highly effective and inexpensive desulfurization process which utilizes readily available, durable and inexpensive activated carbons (catalyst impregnated carbons).
- the desulfurization process performed in accordance with the teachings of the present invention provide the following technical advantages over processes presently known in the art:
- Final oxidized sulfur content in the petroleum distillate product can be regulated by a non-miscible solvent that selectively removes oxidized sulfur aromatic compounds and controlling the number of times the distillate is recycled through fresh regenerated carbon.
- a very high-sulfur, low volume bottom product is produced by repeated exposure to the fresh regenerated carbon, thus increasing fuel yields and decreasing waste.
Landscapes
- Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Abstract
Description
- This application claims the benefit of United States Provisional Application No. 60/170,416, filed Dec. 13, 1999, which is herein incorporated by reference in its entirety.
- The present invention relates to a novel process for the removal of sulfur compounds from petroleum distillates by selective adsorption on activated carbon which can be used in petroleum refining for the desulfurization of gasoline, naphtha, kerosene, diesel fuel, fuel oil and other products.
- The production of sulfur-free petroleum distillates is becoming more and more important due to environmental concerns. In particular, diesel fuel is now regulated all over North America to a maximum sulfur level of 500 ppm (Federal Register, Vol. 64, No. 92, May 13, 1999) for highway diesel engines. In Europe and Japan sulfur levels down to 50 ppm or even lower have been proposed. Currently, catalytic hydrodesulfurization is the technology that is practiced in refineries to reduce diesel sulfur to 500 ppm. The high pressures and temperatures associated with hydrodesulfurization and modifications thereof not only significantly increase the cost, they also have the potential to alter desirable characteristics of distillate fuels. Therefore, there is both a strong economic and technical incentive to develop cost effective techniques for sulfur reduction using very mild conditions (e.g., 20° C. to 75° C. temperature and ambient to very low pressures).
- U.S. Pat. No. 5,454,933 teaches a process that uses activated carbon together with catalysts composed of Group VI and Group VIII metals as a polishing desulfurization agent for distillates previously subjected to hydrodesulfurization. U.S. Pat. No. 2,877,176 teaches the use of alkali-doped activated carbon for adsorption of sulfur from distillate fuels followed by washing the carbon with a hot hydrocarbon. However, a complete process for economic sulfur removal by an adsorbent using negligible amounts of activated carbon (impregnating a catalyst within the carbon to create its activation) and other reagents which results in reduced emissions into the environment is not disclosed or described in the prior art.
- The present invention relates to a process for desulfurization of petroleum distillates, in particular diesel fuel separated by distillation into a low sulfur and a high sulfur fraction, using cyclic low temperature adsorption of the high sulfur diesel fraction on commercially available activated carbon (catalytically impregnated carbon) followed by a solvent stripping step, a regeneration (solvent-washing) step and a carbon drying step in a closed loop zero emission system. The desulfurized diesel fuel is then blended with the low-sulfur diesel fraction from the primary crude separation (distillation) step to yield the final desulfurized diesel product and a high-sulfur by product.
- It is an object of the present invention to reduce total sulfur levels in petroleum distillates to less than approximately 500 ppm.
- FIG. 1 is a diagrammatic flowchart of the overall process' concept as provided in accordance with the teachings of the present invention. Specifically FIG. 1 shows the initial process whereby diesel fuel is split into low-sulfur and high-sulfur fractions.
- FIG. 2 is a detailed flowchart of the overall desulfurization process of the high-sulfur fraction as provided in accordance with the teaching of the present invention.
- In one embodiment of the present invention FIG. 1
crude oil 1 is first subjected todistillation 2 to achieve the 3, 4, 5 of whichvarious fractions diesel 3 is one. Diesel typically ranges from approximately C10 to C20 hydrocarbons. Approximately 30% of the diesel fraction from C10 to C13 contains much less sulfur than the heavier fraction (C14 to C20). The high-sulfur 4 fraction is then subjected to the process shown in FIG. 2. - The high-sulfur diesel fraction or diesel feed 21 mixes with the high-sulfur bottom recycle 41 as shown in FIG. 2. The combined
stream 22 enters the sulfur adsorber 43 either co-currently or counter-currently. Thesulfur adsorber 43 consists of a moving-bed of high surface area (between approximately 500 to 1500 m2/g) porous (with most pores in the 10 to 100 Angstrom range) carbon. The diesel fuel is desulfurized and leaves theadsorber 43 as low-sulfur diesel product 23 to be blended with the lowsulfur diesel fraction 3 from FIG. 1. The movingcarbon stream 25 enters asolvent stripper 44 into which a solvent vaporladen nitrogen stream 27 enters and essentially solvent-free nitrogen stream 28 leaves. The carbon 26 (with oil) moves out of thesolvent stripper 44 as stream 26 and enters the oil desorber 45 where it is contacted with liquid solvent and leaving with the desorbed oil asstream 30. The solvent andoil mixture 30 goes to a solvent still 46 and is separated into a high-sulfur bottom stream 42 and asolvent overhead stream 35 that is recycled back to the oil desorber as stream 29. The high-sulfur bottom recycle stream 41 can be recycled to the mix with the diesel asstream 22 to increase the sulfur content of the feed to thesulfur adsorber 43 and reduce the amount of oil carried away in the high-sulfur bottom stream 42. The regenerated carbon leaves the oil desorber asstream 31 and since it contains solvent it enters a solvent desorber 47. The solvent is stripped from the carbon by nitrogen stream 28 and thenitrogen solvent mixture 27 is recirculated back to thesolvent stripper 44. The dry regenerated carbon leaves the solvent desorber as stream 24 and is recycled back to thesulfur adsorber 43. The entire process takes place at pressures ranging from approximately 1-5 atmospheres. - Typical temperatures of operation are provided below:
- Sulfur adsorber 43 25-50° C.
- Solvent stripper 46 25-50° C.
- Oil desorber 45 50-100° C.
- Solvent desorber 47 50-110° C.
- Solvents used in conjunction with the teachings of the present invention include organic solvents with boiling points below the boiling point of the petroleum distillate to be desulfurized.
- In one embodiment of the present invention, the petroleum distillate is diesel fuel having an initial boiling point of approximately 150° C. Toluene is the preferred solvent for desulfurizing diesel fuel. Other acceptable solvents include, but are not limited to, benzene, chlorinated hydrocarbons, hexane and cyclopentane. However, environmental and toxicity concerns may limit the choice of industrially acceptable solvents. Solvents are selected based upon their ability to remove aromatic components of oxidized sulfur.
- The entire process takes place in a closed loop with no emissions. The high-sulfur bottom may carry traces of solvent away and this is made up as stream 48. The modification of crude distillation to split the diesel into two indicated
3 and 4 from FIG. 1 results in a nearly 30% savings in desulfurization because a 30%fractions smaller stream 4 is to be desulfurized. Furthermore, the extremely mild conditions of the desulfurization process present a very cost-effective alternative to hydrodesulfurization. - While the following non-limiting examples utilize diesel fuel as the source of sulfur containing distillates, the present invention can be applied to other distillates. Moreover, the moving-bed is described as the preferred configuration in FIG. 2; however, cyclic fixed-beds, stirred tanks can also be used. The following non-limiting examples will provide the reader, and persons of ordinary skill in the art, a better appreciation and understanding of the present invention.
- The diesel fuels used were gas oil 0.2% S from Saybolt (Diesel #1), L-0, 2-62 premium from Lukoil (Diesel #2), and L-0, 5-62 from Lukoil (Diesel #3). The properties of these fuels as provided by the supplier are shown in Table 1.
- The following commercially available carbon sources were used as adsorbents:
- A. Carbo-Tech GMBH, Activekohle, Typ D52/4NOx
- B. Calgon Mixed BPL 6×16 and PCB 6×16
- C. Barneby and Sutcliffe, Type GI, 8×16, Lot #1-31-1T
- D. Strem, 06-0050, Lot #135211-S
- E. Calgon, Sample #3092-4-3 (high catalytic activity carbon)
- F. Calgon, BPL 6×16
- G. Calgon, F-400
- H. Calgon, Cal 12×40
- I. Calgon, CPG 12×40
- Horiba Sulfur-in-Oil Analyzer SLFA-20.
-
Diesel # 1 was analyzed 10 times using the Horiba analyzer. The average sulfur content was 1353 ppm with a standard deviation of 18 ppm. - The
Diesel # 2 was analyzed 10 times using the Horiba analyzer. The average sulfur content was 1969 ppm with a standard deviation of 12 ppm. -
Diesel # 3 was analyzed 10 times using the Horiba analyzer. The average sulfur content was 2847 ppm with a standard deviation of 26 ppm. - A quantity of 531.5 g of
Diesel # 3 measurement of 2850-ppm sulfur was vacuum (at 28″ Hg vacuum) distilled to yield 6 fractions. The weight distribution and sulfur content are provided below:Fraction # Weight % Sulfur (ppm) Distilled at (° C.) 1 0.34 57 collected from vapor by condensation at −2 2 9.97 465 172 3 10.47 719 186 4 10.54 1021 197 5 6.91 1304 240 6 (as measured) 60.33 4201 Residual Diesel 6 (by subtraction) 61.82 — — -
TABLE 1 Properties of Diesel Fuels Experimental Designation Diesel # 1 Diesel # 2Diesel # 3Name Gasoil 0.2%S L-0,2-26 Premium L-0,5-62 Supplier Saybolt Lukoil Lukoil Density (kg/L) 0.829 0.860 0.838 Sulfur content (wt %) 0.13 0.19 0.50 Cloud point (C) −9 −3 −6 Cold filter −20 −12 −14 Plugging point (C) Flash point (C) 61 65 65 Fractional Makeup 1 BP (C) 165.6 NA NA 50% recovered (C) 252.5 279 277 95% recovered (C) 342.0 NA NA 96% recovered (C) NM 360 354 FBP (C) 354.5 NA NA - Example 1 was repeated using 467.12 g of
Diesel # 3 that measured at 2850 ppm sulfur. The weight distribution and sulfur contents are provided below.Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.49 230 collected from vapor by condensation at −2 C. 2 10.14 548 170 3 11.27 805 183 4 11.32 1103 195 5 4.21 1405 240 6 (as measured) 61.69 4262 Residual Diesel 6 (by subtraction) 62.57 — — - The residual diesel fractions (#6) from Examples 1 and 2 were combined and subjected to further vacuum distillation into four fractions. The weight distribution and sulfur contents are provided below:
Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 9.09 2004 207 2 8.98 2310 211 3 3.94 2475 217 4 75.33 4780 Residual Diesel 4 (by subtraction) 77.99 — — - Example 1 was repeated using 261.44 g of
Diesel # 1 that measured 1353 ppm sulfur. The weight distributions and sulfur contents are provided below:Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.45 NM collected from vapor by condensation at −2 C. 2 19.88 582 164 3 24.17 828 193 4 20.88 1150 212 5 2.43 1418 223 6 29.19 2574 Residual Diesel - Example 1 was repeated using 470.11 g of
Diesel # 1 that measured 1357 ppm sulfur. Seven fractions were collected. The weight distributions and sulfur contents are provided below.Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.83 379 collected from vapor by condensation at −2 C. 2 10.2 518 143 3 10.63 723 152 4 11.97 795 167 5 9.79 846 181 6 4.15 860 194 7 51.65 1987 Residual Diesel - Example 1 was repeated using 818.69 g of
Diesel # 3 that measured 2850 ppm sulfur. The weight distributions and sulfur contents are provided below:Fraction # Weight % Sulfur (ppm) Distilled at (C) 1 0.85 NM 2 10.94 489 184 3 8.29 622 197 4 9.64 982 203 5 3.77 1123 207 6 66.50 3884 Residual Diesel - A quantity of 41.72 g of residual diesel (3884 ppm sulfur) from Example 6 was placed in each of 5 different beakers. Ten grams of carbons A, B, C, D and E were mixed into the 5 beakers respectively. The sulfur levels in the free oil was measured and the measurements are shown below:
Sulfur remaining (ppm) Carbon After 4.3 h After 24.1 h A — 3904 B — 3071 C — 3065 D — 3134 E 3572 3357 - Unadsorbed residual diesel was decanted from carbons B, C, D, and E of Example 7 and subjected to carbon addition in the same ratio as Example 7. The results of sulfur remaining are shown below:
Decanted Carbon Residual Diesel Added Sulfur remaining (ppm) Carbon (g) (g) After 2.5 h After 23 h B 23.96 5.70 2699 2552 C 22.27 5.37 NM 2553 D 23.39 5.65 NM 2586 E 28.09 6.78 NM 2792 -
Fractions 1 through 5 from Example 6 were combined in a way to yieldBatch # 1 andBatch # 2 with a sulfur measurement of 768 ppm and 694 ppm, respectively. Carbon B was added to each batch in the same oil to carbon ratio as Example 7. The results of the sulfur remaining are shown below:Sulfur remaining (ppm) After 18 h After 41 h Batch # 1 598 603 Batch # 2480 487 - A large sample of
Diesel # 1 was distilled as in Example 1 to produce 5 fractions and 1584 g of residual diesel. 1 and 2 were combined to yield 440 g;Fractions 3, 4, and 5 were combined to yield 1018 g. The residual diesel measured 1992 ppm sulfur. The 1584 g of residual diesel was placed in a 4 L beaker and approximately 396 g of Carbon B was added. After 72 hours, the sulfur content was reduced to 1330 ppm. The resulting diesel was filtered to yield 1313 g of oil with 271 g of oil retained on the carbon. To the 1313 g of diesel, approximately 326 g of fresh Carbon B was added and the slurry which was left standing for 72 hours. The sulfur content was reduced to 980 ppm. The resulting slurry was filtered and 1096 g of oil was recovered. To this oil, 271 g of Carbon F was added and left standing for an additional 24 hours. The sulfur content was reduced to 797 ppm. This slurry was filtered and 880 g of oil was recovered. To this, 222 g of Carbon C was added and left standing for another 24 hours. The sulfur content was reduced to 635 ppm. The resulting slurry was filtered and yielded 689 g of oil. To this, 70 g of Carbon C and 102 g of Carbon D was added. The sulfur reduced to 531 ppm. This final slurry was filtered to yield 554 g of oil.fractions - The combined fractions 3-5 from Example 10 (1018 g) measured 773 ppm sulfur. The combination was placed in a beaker and 252 g of Carbon F was added. After 24 hours the sulfur content had reduced to 612 ppm. The slurry was filtered and 829 g of oil was recovered. To this slurry 206 g of Carbon F was added. After 24 hours the sulfur content had been reduced to 515 ppm. The slurry was filtered and 688 g of oil was recovered. To this 171 g of Carbon D was added. After 24 hours the sulfur content had been reduced to 488 ppm. The slurry was filtered and 570 g of oil was recovered.
- The combined
1 and 2 from Example 10 (440 g) measured 449 ppm sulfur. This combination was mixed with desulfurized oils from Examples 10 and 11 in the same ratio as the original proportions. Thus 554 g of oil from Example 10 was combined with 378 g of oil from Example 11 and 151 g of combinedfractions 1 and 2 to yield desulfurized diesel. The sulfur content of the desulfurized diesel measured at 480 ppm.fractions - Saybolt independently analyzed the desulfurized diesel from Example 12. Properties of the
original Diesel # 1 and desulfurizedDiesel # 1 are compared in Table 2 which illustrates that other than the reduced sulfur content there were no other significant change in properties.TABLE 2 Comparison of Properties of Diesel # 1 andDesulfurized Diesel # 1Result Desulfurized Diesel Diesel Test Method Unit # 1 from Example 13 Specific gravity ASTM D 4052 kg/L 0.8289 0.8147 at 15° C. Sulfur ASTM D 2622 mass % 0.13 0.054 Flash point ASTM D 93 ° C. 61.0 64.0 Cloud point ASTM D 2500 ° C. −9 −15 Cold filter IP 309 ° C. −20 −15 plugging point Distillation IBP ° C. 164.5 174.0 10 v/v recovered ° C. 195.0 200.0 20 v/v recovered ° C. 210.0 213.5 30 v/v recovered ° C. 225.5 228.5 40 v/v recovered ° C. 239.0 241.5 50 v/v recovered ° C. 252.5 254.5 60 v/v recovered ° C. 266.5 267.5 70 v/v recovered ° C. 281.0 281.5 80 v/v recovered ° C. 295.5 299.0 90 v/v recovered ° C. 323.5 322.5 95 v/v recovered ° C. 342.0 342.0 FBP ° C. 354.0 351 Residue v/v % 1.0 2.0 Loss v/v % <0.5 0.5 - A quantity of 182.4 g of Diesel #2 (sulfur-1973 ppm) was mixed with 45.61 of Carbon D and the mixture was left standing for 24 hours. The sulfur content was reduced to 1339 ppm. The slurry was filtered to yield 155 g of oil. To this, 38.7 g of Carbon D was added. The sulfur content was further reduced to 1034 ppm. The slurry was filtered to yield 132.3 g of oil. To this 33 g Carbon D was added. The sulfur content was reduced to 845 ppm. The slurry was filtered to yield 113 g oil. To this 28 g carbon D was added. The sulfur content was reduced to 704 ppm. The slurry was filtered to yield 95 g oil. To this 23.8 g carbon was added. The sulfur content was reduced to 585 ppm. The slurry was filtered to yield 77 g oil. To this 19 g carbon was added. The sulfur content was reduced to 498 ppm. The slurry yield 67 g of desulfurized diesel measuring 498 ppm sulfur.
- A quantity of 72 g of spent carbon (with oil) [from Example 10, Carbon C added to 797 ppm sulfur oil] containing an estimated 33 g oil was subjected to Soxhlet extraction using toluene The toluene (with oil extracted) was distilled to separate the oil that measured 31.5 g and had 1261 ppm sulfur. The carbon was dried with nitrogen gas at 120° C. The regenerated carbon was tested for desulfurization efficiency. Forty-one g of regenerated carbon was mixed with 171 g of
Diesel # 3 containing 2835 ppm sulfur. The sulfur content was reduced to 1949 ppm in 24 hours. The regenerated carbon was thus more efficient than the original carbon. - A quantity of 50 mL of
Diesel # 3 containing 2850 ppm sulfur was mixed with 10 g of carbon G at 22° C. and the sulfur content was monitored as a function of time. The results are shown below:Sulfur remaining Time (h) (ppm) 0.25 2594 0.5 2488 1 2292 2 2219 4 2227 - Same as Example 16 except, 20 g of Carbon G was used. The results are shown below:
Sulfur remaining Time (h) (ppm) 0.25 2033 0.5 1996 1 2002 2 1909 - Same as Example 16 except 50
g Diesel # 3 and 30 g of Carbon G was used. The results are shown below:Sulfur remaining Time (h) (ppm) 0.25 1555 0.5 1754 1.0 1747 2.0 1822 4.0 1720 - Same as Example 18 except 30 g of Carbon F was used. The results are shown below:
Time (h) Sulfur remaining (ppm) 0.08 2384 0.33 2298 0.75 2037 1.0 1997 1.25 1835 3 1731 - Same as Example 18 except sulfur was measured quickly. The results are shown below:
Sulfur remaining Time (min) (ppm) 2 2408 12 2113 24 1882 - Same as Example 18 except 20 g of Carbon H was used. The results are shown below:
Sulfur remaining Time (min) (ppm) 5 2387 17 2223 30 2169 60 2084 130 1974 180 1976 285 1912 - Same as Example 18 except 20 g of Carbon I was used. The results are shown below:
Sulfur remaining Time (min) (ppm) 5 2371 15 2259 40 2148 60 2002 105 1965 210 1929 - Same as Example 18 except 30 g of Carbon I was used. The results are shown below:
Sulfur remaining Time (min) (ppm) 5 2158 30 1880 60 1742 130 1685 180 1660 240 1652 - Same as Example 18 except 30 g of Carbon H was used. The results are shown below:
Sulfur remaining Time (min) (ppm) 5 2120 30 1780 60 1751 120 1686 180 1643 240 1658 - A quantity of 50 g of Diesel #3 (2850 ppm sulfur) was mixed with approximately 20 g of Carbon G. After 15 minutes of contact with stirring, the slurry was filtered with a recovery of 33 g of diesel. Its sulfur value had dropped to approximately 2201 ppm and 17 g of
Diesel # 3 remained attached to the wet carbon externally (in between granules) and inside the pores. Theoriginal Diesel # 3 color was yellow and the diesel recovered was yellow. Fifty (50) g of hexane was poured through the wet carbon and 41 g of hexane wash came through the carbon with 9 g remaining on the carbon. The hexane wash was clear, not yellow, and contained approximately 422 ppm sulfur. Fifty (50) g of toluene was then poured through the wet carbon that had been treated with hexane as above. Forty-three (43) g of toluene wash came through the carbon with 7 g remaining on the carbon. The solvent wash was yellow and contained 291 ppm sulfur. This example illustrates that a more polar and aromatic solvent such as toluene as opposed to hexane recovers chromagenic species from the carbon that actually give the diesel the yellow color, where as hexane is not able to recover these species. - Example 25 was repeated except Carbon F was substituted for Carbon G. The diesel recovered from the carbon weighed 36 g. It had 2374 ppm sulfur and its color was yellow. The hexane wash weighed 41 g, it was colorless and had 266 ppm sulfur. The toluene wash weighed 45 g, it was light yellow and it had 218 ppm sulfur.
- An upflow packed-column was prepared containing about 2200-cc (1238 g) of carbon G. The column was a 2.5-inch×36-inch high stainless steel tube. External controlled heat was supplied to the column if necessary to control the bed temperature. The diesel flow to the column was set at 17.2 cc/min. A number of diesel fuel samples were tested.
- A diesel fuel from a gas station containing 483 ppm sulfur was flowed up through the column at 30° C. Adsorption caused the temperature to rise to 68° C. as the diesel flowed up. Once the adsorption wave went through, the temperature dropped back to 30° C. Four samples of desulfurized diesel were collected in 200 cc batches are shown below:
Sulfur (ppm) Batch 160 Batch 279 Batch 3129 Batch 4117 - Thus, the sulfur was reduced from 483 ppm to 60-129 ppm for the first 800 ml of fuel that passed through the column, over about 45 minutes.
- An upflow column was packed in a similar manner as Example 27. A diesel fuel from a gas station was spiked with dibenzothiophene and thianaphthene to achieve a diesel with a sulfur content of 2863 ppm. This fuel was flowed up at 17.2 cc/min. up through the column in a similar manner as Example 27. Adsorption again caused the temperature to rise to 68° C. and then fall back to 30° C. as the wave passed through the column. Ten samples were collected in 230 cc batches. The sulfur contents of these batches and of the column drain collected are shown below.
Sulfur (ppm) Batch 1100 Batch 2347 Batch 3580 Batch 4903 Batch 51145 Batch 6 1390 Batch 7 1630 Batch 8 1762 Batch 9 1930 Batch 10 1958 Column Drain 2731 - This example demonstrates that the first four batches (690 cc) when combined would have a sulfur content of less that 500 ppm and the last six batches (1610 cc) when combined with a portion of the column drain would have a sulfur content of less than 2000 ppm starting from a diesel containing 2863 ppm sulfur.
- First four batches from Example 28 were combined and designated as Sample B. The last six batches from Example 28 were combined with 610 ml of column drain and designated as Sample C. Each combination and the feed diesel (designated as Sample A) were sent to Saybolt for measurement of sulfur and other diesel specs. These results are shown in Table 3. These results show that the sulfur reduction was as measured in Example 28. The Cetane index of the product improved, indicating removal of aromatics. The other specs did not change significantly.
TABLE 3 Comparison of Properties of Feed Diesel (Sample A) and Two Product Diesels (Samples B & C) of Example 28 ASTM RESULT TEST METHOD Sample A Sample B Sample C Gravity, AP1 at 60° F. D-1298 33.3 38.1 34.8 Flash Point, Pensky D-93 145 141 147 Martens, ° F. Cloud Point, ° C./° F. D-2500 −12/10 −13/9 −11/12 Pour Point, ° C./° F. D-97 −21/−6 −18/0 −15/5 Sulfur, x-ray, wt. % D-4294 0.278 0.045 0.185 Water & Sediments D-2709 0.05 0.0 0.05 (vol. %) Cetane Index D-4737 43.9 52.7 46.6 Distillation, 1 BP (° F.) D-86 358 354 357 Rcvd, 10% (° F.) 419 412 418 50% (° F.) 520 513 517 90% (° F.) 611 612 612 End Point (° F.) 678 672 674 Recovery, vol. % 98.5 98.5 98.5 Loss, vol. % 1.4 1.4 1.4 0.1 0.1 0.1 - The sulfided column from Example 27 was regenerated with toluene upflow (13 cc/min) for two hours at 75° C. The sulfur content in the toluene product and column toluene drain indicated a sulfur recovery from the column of 73%. Following the toluene wash, column was purged with nitrogen for two hours at 100° C.
- The partially regenerated column of Example 30 was tested for recovery of desulfurization efficiency. A diesel sample (
Diesel # 2, Table 1) containing 1998 ppm sulfur was flowed up through the column at conditions similar to Example 27. Seven 200 cc batches and the column drain were collected and their sulfur content was measured as follows:Sulfur (ppm) Batch 1462 Batch 2558 Batch 3726 Batch 4881 Batch 5962 Batch 6 1084 Batch 7 1152 Column Drain 1676 - Thus, the sulfur content was reduced from 1998 ppm to as low as 462 ppm, indicating partial regeneration of the column with toluene.
- The column from Example 31 was regenerated again as in Example 30 with toluene followed by a nitrogen purge. Measurement of sulfur in the toluene effluent and column drain indicated an 86% recovery of the sulfur from the column.
- The partially regenerated column of Example 32 was tested using a 526 ppm sulfur-containing diesel feed at conditions similar to Example 27. The first 250-ml effluent contained 413-ppm sulfur and the column drain contained 506-ppm sulfur. Examples 31 and 33 indicate that following regenerations, sulfur removal limit is around 500 ppm. This suggested a modification to the regeneration procedure.
- The column from Example 33 was regenerated as in Example 30 with toluene, however, the nitrogen purge was conducted at a higher temperature of 115° C.
- The partially regenerated column of Example 34 was again tested using the 526-ppm sulfur containing diesel feed at conditions similar to Example 27. The first 280 ml and the next 125 ml sample effluents showed only 300 ppm sulfur as opposed to 413 ppm in Example 33 and the column drain showed 440 ppm as opposed to 506 ppm sulfur in Example 33. This suggests that the 15° C. higher N 2 purge temperature improved the regeneration efficiency of the column.
- The column of Example 35 was regenerated as in Example 34. The partially regenerated column was tested using a 534-ppm sulfur containing diesel feed, in a manner similar to Example 27, except that the column was maintained at 70° C. as opposed to 30° C. in Example 27. A total of 12 samples of the product and the column drain were collected from the effluent as shown below.
Amount (g) Sulfur (ppm) Sample 1178 276 Sample 2184 294 Sample 3171 255 Sample 4173 299 Sample 5178 316 Sample 6 178 325 Sample 7 177 350 Sample 8 174 357 Sample 9 175 356 Sample 10 186 346 Sample 11 191 338 Sample 12 179 392 Column Drain 795 480 - This example shows that the desulfurization efficiency improves at 70° C. since sulfur is consistently removed to less than 350 ppm from 534 ppm for the first seven collections.
- The column from Example 36 was again regenerated as in Example 35 and subjected to diesel feed containing 485 ppm sulfur in a manner similar to Example 27, except that the temperature was 63° C. and flow was reduced from 17.2 ml/min to 6.3 ml/min. A total of 12 samples of the product and the column drain were collected from the effluent as shown below.
Amount (g) Sulfur (ppm) Sample 1129 249 Sample 2117 277 Sample 3116 261 Sample 4121 260 Sample 5123 263 Sample 6 123 278 Sample 7 120 288 Sample 8 131 322 Sample 9 123 293 Sample 10 120 317 Sample 11 121 284 Sample 12 128 354 Column Drain 711 468 - This example shows that a marginal increase in desulfurization efficiency occurs when the flow is lowered from 17.2 ml/min to 6.2 ml/min. The sulfur is reduced from 485 ppm to below 350 ppm in 11 of the first 12 column effluents.
- The present invention provides a simple, mild, highly effective and inexpensive desulfurization process which utilizes readily available, durable and inexpensive activated carbons (catalyst impregnated carbons). The desulfurization process performed in accordance with the teachings of the present invention provide the following technical advantages over processes presently known in the art:
- 1. The initial separation of the crude petroleum distillates into low and high-sulfur fractions limits the volume of distillates to be processed, thus significantly reducing costs.
- 2. Final oxidized sulfur content in the petroleum distillate product can be regulated by a non-miscible solvent that selectively removes oxidized sulfur aromatic compounds and controlling the number of times the distillate is recycled through fresh regenerated carbon.
- 3. The desulfurization process is mild and effective.
- 4. Selective regeneration of the carbon can be accomplished by using different solvents.
- 5. Diesel fuel quality is not adversely effected.
- 6. A very high-sulfur, low volume bottom product is produced by repeated exposure to the fresh regenerated carbon, thus increasing fuel yields and decreasing waste.
- It will be apparent to one of ordinary skill in the art that many changes and modifications can be made in the invention without departing from the spirit or scope of the appended claims.
Claims (19)
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US09/735,839 US6565741B2 (en) | 1999-12-13 | 2000-12-13 | Process for desulfurization of petroleum distillates |
| US10/440,553 US20040007502A1 (en) | 1999-12-13 | 2003-05-15 | Process for desulfurization of petroleum distillates |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US17041699P | 1999-12-13 | 1999-12-13 | |
| US09/735,839 US6565741B2 (en) | 1999-12-13 | 2000-12-13 | Process for desulfurization of petroleum distillates |
Related Child Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US10/440,553 Division US20040007502A1 (en) | 1999-12-13 | 2003-05-15 | Process for desulfurization of petroleum distillates |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| US20020043482A1 true US20020043482A1 (en) | 2002-04-18 |
| US6565741B2 US6565741B2 (en) | 2003-05-20 |
Family
ID=22619770
Family Applications (2)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US09/735,839 Expired - Lifetime US6565741B2 (en) | 1999-12-13 | 2000-12-13 | Process for desulfurization of petroleum distillates |
| US10/440,553 Abandoned US20040007502A1 (en) | 1999-12-13 | 2003-05-15 | Process for desulfurization of petroleum distillates |
Family Applications After (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US10/440,553 Abandoned US20040007502A1 (en) | 1999-12-13 | 2003-05-15 | Process for desulfurization of petroleum distillates |
Country Status (5)
| Country | Link |
|---|---|
| US (2) | US6565741B2 (en) |
| EP (1) | EP1261681A1 (en) |
| AU (1) | AU2091501A (en) |
| EA (1) | EA004903B1 (en) |
| WO (1) | WO2001042397A1 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7744749B2 (en) | 2005-09-08 | 2010-06-29 | Saudi Arabian Oil Company | Diesel oil desulfurization by oxidation and extraction |
| US20100300938A1 (en) * | 2005-09-08 | 2010-12-02 | Martinie Gary D | Process for oxidative conversion of organosulfur compounds in liquid hydrocarbon mixtures |
| US20120131847A1 (en) * | 2005-08-15 | 2012-05-31 | Arizona Chemical Company, Llc | Low sulfur tall oil fatty acid |
| US20140305840A1 (en) * | 2006-10-20 | 2014-10-16 | Saudi Arabian Oil Company | Asphalt composition |
Families Citing this family (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6962683B2 (en) * | 2002-07-15 | 2005-11-08 | Research Triangle Institute | Method of removing and recovering elemental sulfur from highly reducing gas streams containing sulfur gases |
| US20100294698A1 (en) * | 2009-05-20 | 2010-11-25 | Chevron U.S.A., Inc. | Deep desulfurization process |
| US9296960B2 (en) * | 2010-03-15 | 2016-03-29 | Saudi Arabian Oil Company | Targeted desulfurization process and apparatus integrating oxidative desulfurization and hydrodesulfurization to produce diesel fuel having an ultra-low level of organosulfur compounds |
| US20110220550A1 (en) * | 2010-03-15 | 2011-09-15 | Abdennour Bourane | Mild hydrodesulfurization integrating targeted oxidative desulfurization to produce diesel fuel having an ultra-low level of organosulfur compounds |
| US8906227B2 (en) | 2012-02-02 | 2014-12-09 | Suadi Arabian Oil Company | Mild hydrodesulfurization integrating gas phase catalytic oxidation to produce fuels having an ultra-low level of organosulfur compounds |
| US8920635B2 (en) | 2013-01-14 | 2014-12-30 | Saudi Arabian Oil Company | Targeted desulfurization process and apparatus integrating gas phase oxidative desulfurization and hydrodesulfurization to produce diesel fuel having an ultra-low level of organosulfur compounds |
| WO2015143451A1 (en) * | 2014-03-21 | 2015-09-24 | Eldec Corporation | Tire pressure cold check system |
| CN107774268B (en) * | 2016-08-29 | 2020-07-10 | 中国石油化工股份有限公司 | Method for recycling activated carbon-based desulfurizer |
Family Cites Families (36)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US2733190A (en) * | 1956-01-31 | Treatment of sulphur-containing | ||
| US1950735A (en) * | 1931-03-05 | 1934-03-13 | Universal Oil Prod Co | Process for desulphurizing hydrocarbon oils |
| US1998863A (en) | 1932-05-10 | 1935-04-23 | Phillips Petroleum Co | Process for desulphurizing mercaptan-bearing oil |
| US2324927A (en) | 1941-02-24 | 1943-07-20 | Standard Oil Dev Co | Refining of mineral oils |
| US2470339A (en) * | 1945-07-30 | 1949-05-17 | California Research Corp | Continuous adsorption process |
| GB763625A (en) | 1953-02-06 | 1956-12-12 | Gelsenberg Benzin Ag | Improvements in or relating to the purification of hydrocarbons |
| BE527750A (en) * | 1953-04-02 | |||
| US2908639A (en) * | 1955-06-16 | 1959-10-13 | Texaco Inc | Method for the regeneration of zeolite molecular sieve solid selective adsorbents |
| US2877176A (en) | 1956-09-20 | 1959-03-10 | Standard Oil Co | Process for removing sulfur and aromatics from hydrocarbons using active carbon impregnated with alkali metals or oxides thereof as adsorbent |
| US2966453A (en) | 1959-03-13 | 1960-12-27 | Universal Oil Prod Co | Oxidation of mercapto compounds |
| US3413307A (en) * | 1965-05-10 | 1968-11-26 | Exxon Research Engineering Co | Desulfurization process |
| US3440164A (en) * | 1965-09-03 | 1969-04-22 | Exxon Research Engineering Co | Process for desulfurizing vacuum distilled fractions |
| US3551328A (en) * | 1968-11-26 | 1970-12-29 | Texaco Inc | Desulfurization of a heavy hydrocarbon fraction |
| US3964994A (en) * | 1969-11-28 | 1976-06-22 | Marathon Oil Company | H2 O2 -containing micellar dispersions |
| US3725299A (en) * | 1970-08-06 | 1973-04-03 | Union Carbide Corp | Regeneration of molecular sieves having sulfur compounds adsorbed thereon |
| US4097244A (en) * | 1976-12-13 | 1978-06-27 | Atlantic Richfield Company | Process for removing sulfur from coal |
| US4124531A (en) * | 1977-01-03 | 1978-11-07 | Uop Inc. | Catalytic composite for the treatment of sour petroleum distillates |
| US4105416A (en) * | 1977-04-12 | 1978-08-08 | Atlantic Richfield Company | Process for removing sulfur from coal |
| US4243551A (en) | 1978-12-04 | 1981-01-06 | Ashland Oil, Inc. | Catalyst for oxidizing mercaptans and mercaptide compounds and method for preparing |
| US4250022A (en) | 1979-08-15 | 1981-02-10 | Uop Inc. | Catalytic oxidation of mercaptan in petroleum distillate |
| US4378305A (en) | 1980-12-10 | 1983-03-29 | Uop Inc. | Catalytic composite particularly useful for the oxidation of mercaptans and the removal of gums contained in a sour petroleum distillate |
| US4548705A (en) * | 1982-03-09 | 1985-10-22 | Union Oil Company Of California | Hydrocracking with catalytically active amorphous silica and zeolites |
| US4481107A (en) | 1984-04-06 | 1984-11-06 | Uop Inc. | Oxidation of difficultly oxidizable mercaptans |
| US4675100A (en) | 1985-05-30 | 1987-06-23 | Merichem Company | Treatment of sour hydrocarbon distillate |
| US4824818A (en) | 1988-02-05 | 1989-04-25 | Uop Inc. | Catalytic composite and process for mercaptan sweetening |
| US4990242A (en) * | 1989-06-14 | 1991-02-05 | Exxon Research And Engineering Company | Enhanced sulfur removal from fuels |
| US5310479A (en) * | 1991-12-04 | 1994-05-10 | Mobil Oil Corporation | Process for reducing the sulfur content of a crude |
| US5454933A (en) | 1991-12-16 | 1995-10-03 | Exxon Research And Engineering Company | Deep desulfurization of distillate fuels |
| US5633216A (en) | 1992-03-03 | 1997-05-27 | Institut Francais Du Petrole | Process for sweetening petroleum cuts without regular addition of alkaline solution using a basic solid catalyst |
| JP3227521B2 (en) | 1992-04-06 | 2001-11-12 | 舟越 泉 | Method for recovering organic sulfur compounds from liquid oil |
| US5413704A (en) * | 1993-11-15 | 1995-05-09 | Uop | Process for sweetening a sour hydrocarbon fraction using a mixture of a supported metal chelate and a solid base |
| US5741415A (en) | 1994-09-27 | 1998-04-21 | Chevron U.S.A. Inc. | Method for the demercaptanization of petroleum distillates |
| US5726118A (en) | 1995-08-08 | 1998-03-10 | Norit Americas, Inc. | Activated carbon for separation of fluids by adsorption and method for its preparation |
| US5730860A (en) * | 1995-08-14 | 1998-03-24 | The Pritchard Corporation | Process for desulfurizing gasoline and hydrocarbon feedstocks |
| US5961820A (en) * | 1998-05-27 | 1999-10-05 | Ds2 Tech, Inc. | Desulfurization process utilizing an oxidizing agent, carbonyl compound, and hydroxide |
| EA200200671A1 (en) * | 1999-12-13 | 2002-12-26 | Дс2 Тек, Инк. | METHOD FOR DEMERCAPTANIZATION OF OIL DISTILLATES |
-
2000
- 2000-12-13 EA EA200200668A patent/EA004903B1/en not_active IP Right Cessation
- 2000-12-13 WO PCT/US2000/033707 patent/WO2001042397A1/en not_active Ceased
- 2000-12-13 EP EP00984268A patent/EP1261681A1/en not_active Withdrawn
- 2000-12-13 US US09/735,839 patent/US6565741B2/en not_active Expired - Lifetime
- 2000-12-13 AU AU20915/01A patent/AU2091501A/en not_active Abandoned
-
2003
- 2003-05-15 US US10/440,553 patent/US20040007502A1/en not_active Abandoned
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20120131847A1 (en) * | 2005-08-15 | 2012-05-31 | Arizona Chemical Company, Llc | Low sulfur tall oil fatty acid |
| US7744749B2 (en) | 2005-09-08 | 2010-06-29 | Saudi Arabian Oil Company | Diesel oil desulfurization by oxidation and extraction |
| US20100300938A1 (en) * | 2005-09-08 | 2010-12-02 | Martinie Gary D | Process for oxidative conversion of organosulfur compounds in liquid hydrocarbon mixtures |
| US8715489B2 (en) | 2005-09-08 | 2014-05-06 | Saudi Arabian Oil Company | Process for oxidative conversion of organosulfur compounds in liquid hydrocarbon mixtures |
| US9499751B2 (en) | 2005-09-08 | 2016-11-22 | Saudi Arabian Oil Company | Process for oxidative conversion of organosulfur compounds in liquid hydrocarbon mixtures |
| US20140305840A1 (en) * | 2006-10-20 | 2014-10-16 | Saudi Arabian Oil Company | Asphalt composition |
Also Published As
| Publication number | Publication date |
|---|---|
| AU2091501A (en) | 2001-06-18 |
| EP1261681A1 (en) | 2002-12-04 |
| EA200200668A1 (en) | 2003-06-26 |
| US6565741B2 (en) | 2003-05-20 |
| EA004903B1 (en) | 2004-08-26 |
| US20040007502A1 (en) | 2004-01-15 |
| WO2001042397A1 (en) | 2001-06-14 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US8986622B2 (en) | Apparatus for upgrading whole crude oil to remove nitrogen and sulfur compounds | |
| US5454933A (en) | Deep desulfurization of distillate fuels | |
| US6338794B1 (en) | Desulfurization with zinc titanate sorbents | |
| JP4290547B2 (en) | Oxygenation process of components for refinery blends of transportation fuels | |
| US6565741B2 (en) | Process for desulfurization of petroleum distillates | |
| AU7629400A (en) | Sorbent composition, process for producing same and use in desulfurization | |
| EA011964B1 (en) | Oxidative desulfurization process | |
| KR20080038208A (en) | Process for the desulfurization of gasolines comprising a desulfurization by adsorption of the light fraction and a hydrodesulfurization of the heavy fraction | |
| AU2002321984A1 (en) | Process for oxygenation of components for refinery blending of transportation fuels | |
| JP4755792B2 (en) | Adsorption process for producing ultra-low sulfur hydrocarbon streams | |
| US8951410B2 (en) | Process for demetallization of whole crude oil | |
| WO2003087269A1 (en) | Improved desulfurization process | |
| KR101973703B1 (en) | Hydrotreating of Aromatic-Extracted Hydrocarbon Streams | |
| DE102004031522B4 (en) | Process for desulfurization of a hydrocarbon charge | |
| US6790344B1 (en) | Liquid-phase adsorption process for removing and concentrating heteroatom compounds in hydrocarbons | |
| JP2006144020A (en) | Desulfurization method of hydrocarbon fraction in simulated moving bed | |
| Tasheva | ADSORPTION PROCESS OF SULPHUR REMOVAL FROM MIDDLE DISTILLATE FRACTIONS USING SORBENT MATERIAL. | |
| CN102241999A (en) | Method of removing sulfur-containing compounds from fuel | |
| US20100187160A1 (en) | Method for purifying mineral oil fractions and device suitable for conducting said method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| AS | Assignment |
Owner name: D$2 TECH, INC., IOWA Free format text: ASSIGNMENT OF ASSIGNORS INTEREST;ASSIGNORS:GANGWAL, SANTOSH K.;WISMANN, WILLIAM;REEL/FRAME:014078/0189 Effective date: 19991216 |
|
| REMI | Maintenance fee reminder mailed | ||
| FEPP | Fee payment procedure |
Free format text: PETITION RELATED TO MAINTENANCE FEES FILED (ORIGINAL EVENT CODE: PMFP); ENTITY STATUS OF PATENT OWNER: SMALL ENTITY |
|
| FEPP | Fee payment procedure |
Free format text: PETITION RELATED TO MAINTENANCE FEES GRANTED (ORIGINAL EVENT CODE: PMFG); ENTITY STATUS OF PATENT OWNER: SMALL ENTITY |
|
| REIN | Reinstatement after maintenance fee payment confirmed | ||
| FP | Lapsed due to failure to pay maintenance fee |
Effective date: 20070520 |
|
| FPAY | Fee payment |
Year of fee payment: 4 |
|
| SULP | Surcharge for late payment | ||
| PRDP | Patent reinstated due to the acceptance of a late maintenance fee |
Effective date: 20070917 |
|
| STCF | Information on status: patent grant |
Free format text: PATENTED CASE |
|
| FPAY | Fee payment |
Year of fee payment: 8 |
|
| FPAY | Fee payment |
Year of fee payment: 12 |